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Systematic Prey Preference by Introduced Mice Exhausts the Ecosystem on Antipodes Island

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Systematic Prey Preference by Introduced Mice Exhausts the Ecosystem on Antipodes Island Biol Invasions (2020) 22:1265–1278 https://doi.org/10.1007/s10530-019-02194-4 (0123456789().,-volV)( 0123456789().,-volV) ORIGINAL PAPER Systematic prey preference by introduced mice exhausts the ecosystem on Antipodes Island James C. Russell . Joanne E. Peace . Melissa J. Houghton . Sarah J. Bury . Thomas W. Bodey Received: 5 August 2018 / Accepted: 10 December 2019 / Published online: 14 January 2020 Ó The Author(s) 2020 Abstract House mice (Mus musculus) are a wide- neighbouring mouse-free offshore islands together spread invasive species on islands. Where they are the with mouse stomach contents and stable isotope sole introduced mammal they can have particularly analyses of mouse livers to examine dietary prefer- strong negative impacts on recipient ecosystems. ences. We identified directly impacted and consumed House mice impacts have been documented on almost invertebrate Orders relative to their abundance and every component of the terrestrial ecosystem on provided a comprehensive picture of resource flow and Southern Ocean islands, including plants, inverte- overlap in the invaded terrestrial ecosystem. The brates, birds and ecosystem function. We undertook a remote terrestrial ecosystem of Antipodes Island was comprehensive study to determine the impacts of tightly circumscribed with strong resource overlap. house mice on Antipodes Island, New Zealand. This Mouse diet varied seasonally with resource availabil- study was done prior to mouse eradication to inform ity, dominated by invertebrates and land birds in monitoring and restoration. We used invertebrate summer, and plants and seabirds in winter. Inverte- pitfall trapping on the main Antipodes Island and brates that were preferentially preyed upon were Amphipoda, Lepidoptera and some species of Coleop- tera. These patterns suggest the ecosystem is annually J. C. Russell (&) Á J. E. Peace Á T. W. Bodey (&) School of Biological Sciences, University of Auckland, driven by a seasonal bottom-up resource pulse over Auckland 1142, New Zealand summer, where mice are a selective predator, differ- e-mail: [email protected] entially preying on invertebrates relative to inverte- T. W. Bodey brate abundance. Mice appear to be exhausting e-mail: [email protected] preferred prey as they systematically consume their way through the terrestrial ecosystem. Land bird M. J. Houghton Centre for Biodiversity and Conservation Science, School diet also varied seasonally and some of these birds of Biological Sciences, The University of Queensland, likely competed with mice for invertebrate prey. St. Lucia, QLD 4072, Australia Eradication of mice from Antipodes Island should reduce the predation on invertebrates and reduce the S. J. Bury National Institute of Water and Atmospheric Research effects of competition and predation on land birds. Ltd., Greta Point, Hataitai, Wellington 6021, New This should have flow-on effects to the abundance of Zealand invertebrates and endemic land bird sub-species of pipit and snipe. T. W. Bodey Environment and Sustainability Institute, University of Exeter, Penryn TR10 9FE, UK 123 1266 J. C. Russell et al. Keywords Diet Á House mouse Á Mus musculus Á The Antipodes Islands exhibit high levels of Southern Ocean Á Invertebrates Á Stable isotopes Á invertebrate endemism (Marris 2000). There are 23 Stomach content native Coleoptera species with nine island endemics (Marris 2000) and 19 Lepidoptera species with four island endemics (Patrick 1994). The main Antipodes Island lacks medium-sized flightless invertebrates, Introduction and mice have been invoked as the reason (Patrick 1994). For example, an undescribed weta species House mice (Mus musculus) are a widespread invasive (Orthoptera) is known from mouse-free offshore species and one of the most commonly introduced Bollons Island, but has not been collected from the rodent species to islands (Moors and Atkinson 1984; main Antipodes Island (Marris 2000; McIntosh 2001). Angel et al. 2009). They are hardy and adaptive with Investigations by Marris (2000) and Russell (2012) plastic dietary requirements allowing them to suc- inferred that mice impacted on the abundance, com- cessfully adapt to and establish themselves in a variety position, and distribution of the invertebrate fauna on of habitats (e.g. Renaud et al. 2015). Ecosystems Antipodes Island, but these investigations did not invaded by mice suffer various impacts, from seed directly study mouse diet. predation to attack of seabirds (Angel et al. 2009;St In this study, we initiated investigations to further Clair 2011; Bolton et al. 2014; Cuthbert et al. 2016), to clarify the impacts of mice on the main Antipodes altered ecosystem function (Eriksson and Eldridge Island, prior to their eradication in winter 2016 (Horn 2014). On subantarctic islands, mice consume most of et al. 2018). We combined invertebrate pitfall trapping the food items available (Le Roux et al. 2002). with stomach contents and stable isotope analyses to However, invertebrates are a favoured prey item, and determine: (1) what are the major resources for mice mice can contribute to their decline and even extinc- on Antipodes Island? (2) which invertebrates have tion (Rowe-Rowe et al. 1989; Le Roux et al. 2002; been most impacted by mice compared to uninvaded Smith et al. 2002). Through their predation of offshore islands? and (3) which invertebrates are invertebrates, mice may also compete with insectiv- preferentially targeted as prey? Together this allowed orous birds and impact on ecosystem function and us to make predictions about anticipated species trophic links (Huyser et al. 2000; Marris 2000;Le recoveries following mouse eradication. This work Roux et al. 2002; Miskelly et al. 2006). was undertaken over the course of three field trips: The Antipodes Islands in the New Zealand sub- summer (January) 2011, winter (July) 2013, and antarctic region are remote, but mice have been autumn and winter (April to July) 2016. present as the sole invasive mammal since the early 1900s. Given their unique genetics in New Zealand, the founders are likely to have been from the Methods shipwreck of the President Felix Faure (Veale et al. 2018). Since colonisation, they have spread across the Study site entire main Antipodes Island, but have never been detected on nearby islands and rock stacks (Russell The Antipodes Islands (2097 ha; 49° 410 S; 178° 480 E) 2012). They were found to be ‘‘abundant at all lie 872 km south-east of New Zealand (Fig. 1). The altitudes’’ in 1969 (Warham and Johns 1975), but climate is characterised by strong south-westerly Marris (2000) noted that mouse abundance decreased winds with frequent cloud, fog and rain, and cool with increasing altitude. Density of mice on Antipodes temperatures (2–13 °C) with little seasonal variation Island was estimated at around 50–100/ha (Russell (Taylor 2006). The island group is an important and 2012; Elliot et al. 2015). Due to the unique ecosystem diverse breeding site for seabirds, and two species of and isolation of Antipodes Island, the impacts of mice endemic parakeets (Cyanoramphus spp.). Vegetation are concerning, particularly as endemic birds, inver- on the main Antipodes Island (2025 ha) is entirely tebrates and plants might constitute major prey items composed of tussock grassland (Poa and Carex spp.) (Moors and Atkinson 1984; Godley 1989; Patrick interspersed with some shrubs (Coprosma spp.) and 1994). ferns (see Godley 1989 for a complete description). 123 Systematic prey preference by introduced mice exhausts the ecosystem on Antipodes Island 1267 178°45’E 178°48’E Archway Island ANTIPODES ISLANDS Locality Map N 0 500 North I km NEW ZEALAND 40 Bollons Island South I Chatham Is Snares Is Bounty Is Antipodes Is Auckland Is 50 Campbell I 160 170 180 49°40’S Anchorage Bay Hut Cove Reef Point Conical Hill 135 Stella Bay Orde Lees Islet North Plains Windward Islands Crater Bay 49°41’S Alert Bay 366 Cave Point Mt. Galloway am Central Plateau tre Southwest Dougall S Leeward Island Plain Mt. Waterhouse 49°42’S Stack Bay 356 Southern Valley Ringdove Stream Ringdove Bay Bay Albatross Point h ut o S 0 1 2 km Fig. 1 Antipodes Islands. Sampling sites are indicated by asterisks Five study sites were focused upon. At the north-east locations with dense tussock vegetation reaching end of the island Anchorage Bay, Hut Creek and Reef 2 m in height; whereas the more distant higher altitude Point sites are neighbouring low altitude coastal North Plains plateau site supports lower vegetation of 123 1268 J. C. Russell et al. 0.5 m height made up of separated cushion plants vegetation, and unknown material were estimated (Russell 2012). The fifth study site was the summit of visually under a binocular microscope. Then the the highest point on the island, Mt Galloway. invertebrate portion was examined under a binocular microscope to determine the minimum number of Pitfall trapping representatives of each Order as calculated from identifiable remains. Identification was made through Surface invertebrates were pitfall trapped at Anchor- reference to invertebrate collections held at the age Bay, Reef Point, Hut Creek, the North Plains and University of Auckland and voucher specimens are the summit of Mt Galloway in summer (January) lodged at the Auckland War Memorial Museum. 2011, winter (July) 2013 and winter (June) 2016 and These data were used to determine mouse preference on the mouse-free offshore islands of Bollons and for different invertebrate Orders as reflected by Leeward in winter (July) 2016. At each site, ten pitfall proportional
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